CN110204714B - Magnetic covalent triazine framework material and preparation method and application thereof - Google Patents

Magnetic covalent triazine framework material and preparation method and application thereof Download PDF

Info

Publication number
CN110204714B
CN110204714B CN201910540881.9A CN201910540881A CN110204714B CN 110204714 B CN110204714 B CN 110204714B CN 201910540881 A CN201910540881 A CN 201910540881A CN 110204714 B CN110204714 B CN 110204714B
Authority
CN
China
Prior art keywords
covalent triazine
framework material
magnetic
magnetic covalent
terephthalonitrile
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201910540881.9A
Other languages
Chinese (zh)
Other versions
CN110204714A (en
Inventor
高仕谦
邵子纯
卢建
张占恩
丁炜楠
刘婷婷
王俊霞
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Suzhou University of Science and Technology
Original Assignee
Suzhou University of Science and Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Suzhou University of Science and Technology filed Critical Suzhou University of Science and Technology
Priority to CN201910540881.9A priority Critical patent/CN110204714B/en
Publication of CN110204714A publication Critical patent/CN110204714A/en
Application granted granted Critical
Publication of CN110204714B publication Critical patent/CN110204714B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/28Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/33Electric or magnetic properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/61310-100 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/63Pore volume
    • B01J35/633Pore volume less than 0.5 ml/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/64Pore diameter
    • B01J35/6472-50 nm
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08GMACROMOLECULAR COMPOUNDS OBTAINED OTHERWISE THAN BY REACTIONS ONLY INVOLVING UNSATURATED CARBON-TO-CARBON BONDS
    • C08G73/00Macromolecular compounds obtained by reactions forming a linkage containing nitrogen with or without oxygen or carbon in the main chain of the macromolecule, not provided for in groups C08G12/00 - C08G71/00
    • C08G73/06Polycondensates having nitrogen-containing heterocyclic rings in the main chain of the macromolecule
    • C08G73/0622Polycondensates containing six-membered rings, not condensed with other rings, with nitrogen atoms as the only ring hetero atoms
    • C08G73/0638Polycondensates containing six-membered rings, not condensed with other rings, with nitrogen atoms as the only ring hetero atoms with at least three nitrogen atoms in the ring
    • C08G73/0644Poly(1,3,5)triazines
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/18Oxygen-containing compounds, e.g. metal carbonyls
    • C08K3/20Oxides; Hydroxides
    • C08K3/22Oxides; Hydroxides of metals
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/343Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the pharmaceutical industry, e.g. containing antibiotics
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K3/00Use of inorganic substances as compounding ingredients
    • C08K3/18Oxygen-containing compounds, e.g. metal carbonyls
    • C08K3/20Oxides; Hydroxides
    • C08K3/22Oxides; Hydroxides of metals
    • C08K2003/2265Oxides; Hydroxides of metals of iron
    • C08K2003/2275Ferroso-ferric oxide (Fe3O4)
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08KUse of inorganic or non-macromolecular organic substances as compounding ingredients
    • C08K2201/00Specific properties of additives
    • C08K2201/01Magnetic additives

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Compounds Of Iron (AREA)

Abstract

The invention relates to a magnetic covalent triazine framework material and a preparation method and application thereof, wherein the magnetic covalent triazine framework material comprises a covalent triazine framework and Fe3O4. The magnetic covalent triazine framework material has magnetism, is convenient to recycle, can be used for wastewater treatment, and can be used as a catalyst for degradation of antibiotics. The preparation method of the invention adopts microwave as heat source and Fe3O4As microwave absorbing and transmitting medium, the terephthalonitrile can be rapidly condensed, and simultaneously, Fe3O4The existence of (2) enables the powder to be gathered in the reaction process, and the powder overflow phenomenon is not easy to generate, so that the reaction is more complete.

Description

Magnetic covalent triazine framework material and preparation method and application thereof
Technical Field
The invention particularly relates to a magnetic covalent triazine framework material and a preparation method and application thereof.
Background
A Covalent Organic Frameworks (COFs) is a novel high-performance carbonaceous high polymer material which is composed of light elements (H, O, C, N, B) through Covalent bonds with strong bonding force (such as C-C, C-N, C-O and the like), and has high chemical stability in different solvents due to the existence of the Covalent bonds. Covalent triazine-based Frameworks (CTFs) are a class of branches of COFs, and are long-chain polymers having rigid hydrophobic aromatic Frameworks and polar functional groups prepared by using aromatic nitriles as raw materials and ZnCl2The catalyst is prepared by trimerization condensation, and has attracted attention because of no need of organic solvent, low cost, high nitrogen content and the like. The conventional thermal synthesis method requires harsh conditions, requires a long reaction time (20-116h) under the conditions of high temperature and high pressure (400-. The microwave synthesis technology is frequently applied to the field of material preparation due to the advantages of simple operation, short reaction time, high energy utilization rate and the like.
However, the performance of the covalent triazine skeleton material in the prior art still needs to be improved, and in the application process, the problem that the covalent triazine skeleton material is difficult to recover exists.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provide a magnetic covalent triazine framework material, a preparation method and application thereof.
In order to solve the technical problems, the invention adopts the following technical scheme:
the invention provides a magnetic covalent triazine framework material which comprises a covalent triazine framework and Fe3O4
The magnetic covalent triazine framework material is in a regular tetrahedron shape.
The magnetic covalent triazine framework material has superparamagnetism. According to a preferred embodiment, said magnetic covalent triazine backbone material has a saturation magnetization of more than 70emu g-1
The magnetic covalent triazine framework material of the invention has pores, and further, the magnetic covalent triazine framework material has larger pore diameter and smaller pore volume. According to a preferred embodiment, the pore diameter of the magnetic covalent triazine framework material is 6-8 nm, and the pore volume is 0.02-0.04 cm3·g-1
According to a preferred embodiment, the surface of the magnetic covalent triazine framework material comprises 46-56% by mass of carbon atoms, 5.5-6.6% by mass of nitrogen atoms, 28-36% by mass of oxygen atoms, 8.9-10.9% by mass of iron atoms and 1.2-1.4% by mass of zinc atoms.
In the invention, the magnetic covalent triazine framework material is powdery.
The invention also provides a preparation method of the magnetic covalent triazine framework material, and the magnetic covalent triazine framework material is prepared from terephthalonitrile and Fe3O4In ZnCl2Under the action of microwave, the product is obtained.
In the invention, Fe is adopted3O4The microwave absorbing and transmitting medium is used together with microwaves, so that the reaction temperature can be ensured to carry out the reaction; in addition, by adjusting different microwave output powers, the microwave power is adjustedThe properties of the generated magnetic covalent triazine framework material are different, so that the magnetic covalent triazine framework material can be applied to different fields.
Preferably, the output power of the microwave is 300-600W, so that the reaction can be fully performed, and the utilization rate of raw materials is improved.
Preferably, said terephthalonitrile and Fe3O4The charging molar ratio of (a) to (b) is 1:0.5 to 1.2, and more preferably 1:1 to 1.2. The product performance can be better by adopting the feeding molar ratio while taking the yield into consideration.
Preferably, said terephthalonitrile and said ZnCl2The feeding mass ratio of (A) to (B) is 1: 5-10. The residual quantity of the zinc salt in the product can be reduced by adopting the mass ratio while taking the yield into consideration.
According to a preferred and specific embodiment, the preparation method is as follows: reacting said terephthalonitrile, said Fe3O4And said ZnCl2And after mixing, reacting for 30-90 min under the microwave power of 300-600W, soaking with hydrochloric acid, separating precipitates under the condition of an external magnetic field, and washing and drying the precipitates to obtain the magnetic covalent triazine framework material.
The third aspect of the invention provides the application of the magnetic covalent triazine framework material in wastewater treatment.
In particular, the magnetic covalent triazine framework material adsorbs harmful substances such as methylene blue, dye and the like in wastewater.
The third aspect of the invention provides the application of the magnetic covalent triazine skeleton material in the degradation of antibiotics, wherein the magnetic covalent triazine skeleton material and an oxidant are added when the degradation of the antibiotics is carried out.
Wherein, the magnetic covalent triazine framework material is used as a catalyst.
The raw materials in the present invention may be commercially available, or Fe in the present invention3O4Prepared by a hydrothermal method.
Hydrothermal method for preparing Fe3O4Specific method of (1)Comprises the following steps: 6.74g FeCl was weighed3·6H2And placing the O into 125mL of ethylene glycol, stirring for 30min to obtain a homogeneous solution, adding 14.37g of sodium acetate, continuously stirring for 30min, uniformly mixing, transferring the mixed solution into a 200mL high-pressure reaction kettle, and reacting for 8h at 200 ℃. After cooling to room temperature, the black magnetic microspheres were collected with a magnet, washed three times with water and ethanol alternately, vacuum dried at 60 ℃ for 6h, and ground for future use.
Due to the implementation of the technical scheme, compared with the prior art, the invention has the following advantages:
the magnetic covalent triazine framework material has magnetism, is convenient to recycle, can be used for wastewater treatment, and can be used as a catalyst for degradation of antibiotics.
The preparation method of the invention adopts microwave as heat source and Fe3O4As microwave absorbing and transmitting medium, the terephthalonitrile can be rapidly condensed, and simultaneously, Fe3O4The existence of (2) enables the powder to be gathered in the reaction process, and the powder overflow phenomenon is not easy to generate, so that the reaction is more complete.
Drawings
FIG. 1 is an SEM (left) and TEM (right) image of MCTF obtained in example 5;
FIG. 2 is an FTIR spectrum of MCTF and terephthalonitrile (DCB) obtained in example 5;
FIG. 3 is an XRD pattern of MCTF obtained from example 5;
FIG. 4 is a magnetization curve of MCTF obtained in example 5;
FIG. 5 is an XPS plot of MCTF obtained in example 5;
FIG. 6 is a graph showing N in MCTF obtained in example 52Adsorption-desorption isotherms;
FIG. 7 shows MCTF, DCB and Fe3O4Adsorption rate curve to AO 7;
FIG. 8 shows the degradation trend of SMX in different systems;
figure 9 is a graph of the tendency of MCTF prepared in various examples to catalyze PMS to degrade SMX.
Detailed Description
The technical solution of the present invention will be described in further detail below with reference to specific embodiments.
Fe described below3O4From Mecline I811693-500 g; terephthalonitrile was purchased from alatin D111053; zinc chloride was purchased from Meclin Z820755. The following examples employ microwave equipment from Shanghai New Instrument microwave chemistry, Inc. (Uwave-2000).
Example 1
Weighing 2g of terephthalonitrile and 2g of Fe3O4Mixing uniformly, and quickly adding 16g ZnCl2Uniformly mixing, transferring the powder into a quartz crucible, reacting for 60min under the power of 500W to obtain a black product, and reacting with the black product at the power of 0.1 mol.L-1HCl soak to remove residue while preventing ZnCl2Hydrolyzing, separating precipitate under the condition of external magnetic field after soaking, washing with water and anhydrous ethanol alternately for three times, vacuum drying at 60 deg.C for 6 hr, taking out, and grinding to obtain 0.85g MCTF powder.
Example 2
Weighing 2g of terephthalonitrile and 4g of Fe3O4Mixing uniformly, and quickly adding 16g ZnCl2Uniformly mixing, transferring the powder into a quartz crucible, reacting for 60min under the power of 300W to obtain a black product, and reacting with the black product at the power of 0.1 mol.L-1HCl soak to remove residue while preventing ZnCl2Hydrolyzing, separating precipitate under the condition of external magnetic field after soaking, washing with water and anhydrous ethanol alternately for three times, vacuum drying at 60 deg.C for 6h, taking out, and grinding to obtain 2.93g MCTF powder.
Example 3
Weighing 2g of terephthalonitrile and 4g of Fe3O4Mixing uniformly, and quickly adding 16g ZnCl2Uniformly mixing, transferring the powder into a quartz crucible, reacting for 60min under 400W power to obtain a black product, and reacting with the black product at 0.1 mol.L-1HCl soak to remove residue while preventing ZnCl2Hydrolyzing, separating precipitate under the condition of external magnetic field after soaking, washing with water and anhydrous ethanol alternately for three times, vacuum drying at 60 deg.C for 6 hr, taking out, and grinding to obtain 2.68g MCTF powder.
Example 4
Weighing 2g of terephthalonitrile and 4g of Fe3O4Mixing uniformly, and quickly adding 16g ZnCl2Uniformly mixing, transferring the powder into a quartz crucible, reacting for 60min under the power of 500W to obtain a black product, and reacting with the black product at the power of 0.1 mol.L-1HCl soak to remove residue while preventing ZnCl2Hydrolyzing, separating precipitate under the condition of external magnetic field after soaking, washing with water and anhydrous ethanol alternately for three times, vacuum drying at 60 deg.C for 6h, taking out, and grinding to obtain 1.54g MCTF powder.
Example 5
Weighing 2g of terephthalonitrile and 4g of Fe3O4Mixing uniformly, and quickly adding 16g ZnCl2Uniformly mixing, transferring the powder into a quartz crucible, reacting for 60min under 600W power to obtain a black product, and reacting with the black product at the power of 0.1 mol.L-1HCl soak to remove residue while preventing ZnCl2Hydrolyzing, separating precipitate under the condition of external magnetic field after soaking, washing with water and anhydrous ethanol alternately for three times, vacuum drying at 60 deg.C for 6h, taking out, and grinding to obtain 1.24g MCTF powder.
The SEM and TEM of the MCTF powder are shown in FIG. 1, and it can be seen that the powder is in the form of regular tetrahedrons with well-defined corners and clearly visible boundary marks.
Analysis of functional groups of MCTF and the starting material DCB by FTIR, as shown in FIG. 2, the DCB starting material for the synthesis of MCTF contained a-C.ident.N bond, and therefore had a spectrum of 2232cm in DCB-1Has obvious vibration peak, compared with MCTF which has no vibration peak at 1613cm-1And 1411cm-1The peak appears when the C-N bond and the C-C bond vibrate, which proves that the triazine ring exists and the trimerization reaction is completed, 588cm-1The peak is Fe-O vibration peak.
In order to investigate the composition of the ferrite compounds, XRD of MCTF was analyzed as shown in FIG. 3, showing strong diffraction peaks at diffraction angles of 18.3 °, 30.4 °, 35.4 °, 37 °, 43 °, 53.3 °, 56.8 °, 62.4 °, peak positions corresponding to Fe3O4Standard cards (JCPDS75-1609) conform to, which correspond to Fe respectively3 O 4111, 220, 311, 222, 400, 422, 511, and 440 of MCTF, it was confirmed that the magnetic iron oxide contained in MCTF was Fe3O4
By measuring the saturation magnetization of MCTF at room temperature, as shown in FIG. 4, it can be seen that there is no obvious hysteresis loop, the magnetization curve is S-shaped, no hysteresis phenomenon occurs, and the material shows good superparamagnetism. The saturation magnetization of MCTF was 75.14emu g-1And has good magnetic performance.
FIG. 5 is an XPS diagram of MCTF, in which 284.1eV, 398.1eV and 530.1eV, three peaks with stronger signals appear, which correspond to the bonding energies of C1s, N1s and O1s in MCTF, and show that the main elements of the surface of the material are carbon, nitrogen and oxygen. Meanwhile, a weaker Zn2p peak appears at 1021.1, which indicates that excessive ZnCl exists in the material synthesis process2So that a certain amount of ZnCl remains even by washing with hydrochloric acid for a long time2. The atomic mass percentages of the MCTF are shown in Table 1, and it can be seen from Table 1 that the material contains ZnCl2 residue, but the atomic mass of Zn is only 1.31%.
TABLE 1
Name (R) C N O Fe Zn
Atomic mass% 50.63 6.05 32.15 9.85 1.31
The porosity of MCTF was evaluated by nitrogen uptake experiments at 77K, and FIG. 6 shows the N of MCTF2Adsorption-desorption isotherms, which showed the isotherm of type IV, were observed, and the presence of a hysteresis loop was confirmed, demonstrating that the material has a large number of micropores and a BET specific surface area of 93.6131m2·g-1But has a pore diameter of 6.93nm and a pore volume of 0.03cm3·g-1The larger pore size and smaller pore volume of the material enable the material to have the potential of storing substances and maintaining the activity of the substances.
Application example 1 methylene blue adsorption experiment
5mL of methylene blue (10 mg. L) was taken-1) 10mg of the MCTF materials prepared in examples 2 to 5 were added into a centrifuge tube, and after vortexing for 30 seconds, the absorbance of the raffinate was measured by an ultraviolet-visible spectrophotometer, and the absorbance was substituted into a standard curve to calculate the methylene blue concentration of the raffinate, and the adsorption rate was calculated by the following formula, and the results of the adsorption rate of the MCTF materials prepared in each example are shown in Table 2.
Adsorption rate (%) - (c)0-ct)×100/c0
TABLE 2
Example 2 Example 3 Example 4 Example 5
Adsorption rate 57.4% 63.3% 96.9% 93.1%
Application examples 2, AO7 adsorption experiment
100mL of AO7 working solution (10 mg. L) was taken-1) In a conical flask, 0.1 mol.L is used-1HCl and NaOH to adjust the initial pH of the solution. Prepared MCTF (obtained in example 3), DCB and Fe were separately mixed3O4The timing is started when the solution is put into the prepared solution, and the magnetic stirring speed is adjusted to be about 1000 r.min-1The MCTF is thrown out at high speed without being attached to the surface of the rotor and is uniformly distributed in the solution, and 5mL of the solution is taken at different time points and is filtered by a 0.45-micron water system filter film to be measured.
MCTF, DCB and Fe3O4The adsorption rate of AO7 is shown in FIG. 7, wherein T298K and C (AO7) 10 mg.L are measured-1,pH≈7,C(MCTF、DCB、Fe3O4)=0.4g·L-1
Within 20min, terephthalonitrile and Fe3O4The adsorption rates of AO7 were 3.0% and 3.4%, respectively, under the system. From this, it can be seen that the raw materials terephthalonitrile and Fe3O4No significant adsorption on AO 7; compared with the prior art, the MCTF has the adsorption rate of 98.8 percent on AO7 within 20 min.
Application example 3 SMX degradation experiment
At room temperature, a predetermined amount of pure water was poured into a 100mL volumetric flask, and a predetermined amount of Peroxymonosulfate (PMS) and MCTF (obtained in example 4) were added to bring the reaction concentrations to 0.15 mmol.L, respectively-1、0.3g·L-1Subsequently, a certain amount of Sulfamethoxazole (SMX) was added to bring the reaction concentration to 0.5 mmol. multidot.L-1The reaction starts. Samples were taken at different time points, followed by rapid addition of excess quencher Na2S2O3The reaction was stopped and the quenched sample was filtered through a 0.22 μm filter and the filtrate was collected and analyzed by HPLC-MS/MS. For comparative analysis, blanks were PMS alone and MCTF alone. The results are shown in fig. 8, where T298K and c (smx) 0.5mmol · L were measured-1,pH≈7,C(MCTF)=0.3g·L-1,C(PMS)=0.15mmol·L-1
As can be seen from FIG. 8, PMS and MCTF alone have no obvious effect, and PMS added as oxidant and MCTF added as catalyst SMX can be completely degraded within 30 min.
Meanwhile, the MCTF materials prepared in different examples are examined for the effect of catalyzing the PMS to degrade SMX, as shown in FIG. 9, wherein 300W is example 2, 400W is example 3, 500W is example 4, and 600W is example 5, as can be seen from FIG. 9, example 5(600W) has the best effect, and can be completely degraded within 30 min.
The present invention is described in detail in order to make those skilled in the art understand the content and practice the invention, and the invention is not limited to the above embodiments, and all equivalent changes or modifications made according to the spirit of the invention should be covered by the scope of the invention.

Claims (8)

1. A magnetic covalent triazine scaffold material, characterized by: comprising a covalent triazine skeleton and Fe3O4(ii) a The magnetic covalent triazine framework material is prepared from terephthalonitrile and Fe3O4In ZnCl2Under the action of microwave, the magnetic covalent triazine skeleton material is in a regular tetrahedron shape; the magnetic covalent triazine framework material has superparamagnetism, and the saturation magnetization intensity of the material is more than 70emu-1(ii) a The magnetic covalent triazine framework material has pores, the pore diameter of the pore is 6-8 nm, and the pore volume is 0.02-0.04 cm3•g-1
2. A process for the preparation of a magnetic covalent triazine framework material as claimed in claim 1, characterized in thatCharacterized in that: the magnetic covalent triazine framework material is prepared from terephthalonitrile and Fe3O4In ZnCl2Under the action of microwave, the product is obtained.
3. The method of claim 2, wherein: the output power of the microwave is 300-600W.
4. The method of claim 2, wherein: the terephthalonitrile and Fe3O4The feeding molar ratio of (A) to (B) is 1: 0.5-1.2.
5. The method of claim 2, wherein: said terephthalonitrile and said ZnCl2The feeding mass ratio of (A) to (B) is 1: 5-10.
6. The method of claim 2, wherein: the preparation method comprises the following specific implementation modes: reacting said terephthalonitrile, said Fe3O4And said ZnCl2And after mixing, reacting for 30-90 min under the microwave power of 300-600W, soaking with hydrochloric acid, separating precipitates under the condition of an external magnetic field, and washing and drying the precipitates to obtain the magnetic covalent triazine framework material.
7. Use of a magnetic covalent triazine framework material of claim 1 in wastewater treatment.
8. Use of a magnetic covalent triazine scaffold material according to claim 1 for the degradation of antibiotics, wherein said magnetic covalent triazine scaffold material and an oxidizing agent are added during the degradation of antibiotics.
CN201910540881.9A 2019-06-21 2019-06-21 Magnetic covalent triazine framework material and preparation method and application thereof Active CN110204714B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910540881.9A CN110204714B (en) 2019-06-21 2019-06-21 Magnetic covalent triazine framework material and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910540881.9A CN110204714B (en) 2019-06-21 2019-06-21 Magnetic covalent triazine framework material and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN110204714A CN110204714A (en) 2019-09-06
CN110204714B true CN110204714B (en) 2021-12-31

Family

ID=67793921

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910540881.9A Active CN110204714B (en) 2019-06-21 2019-06-21 Magnetic covalent triazine framework material and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN110204714B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111468075B (en) * 2020-04-14 2022-04-08 蚌埠学院 Synthetic method of magnetic triazine-based covalent bond organic framework material and application of magnetic triazine-based covalent bond organic framework material in dye wastewater adsorption
CN113754667B (en) * 2021-09-28 2023-01-10 西湖大学 Method for rapidly and massively preparing high-crystalline semiconductor covalent triazine framework
CN113881041B (en) * 2021-11-18 2023-06-30 西湖大学 Method for preparing high-crystallization high-specific surface area covalent triazine frame in large scale
CN116333308A (en) * 2023-03-15 2023-06-27 华侨大学 Donor-pi-acceptor type covalent triazine framework material and preparation method and application thereof

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4439059A (en) * 1980-07-08 1984-03-27 Asahi Kasei Kogyo Kabushiki Kaisha Artificial reef unit
CN103724234A (en) * 2014-01-03 2014-04-16 万华化学集团股份有限公司 Method for preparing polyisocyanate containing biuret
CN105585711A (en) * 2015-12-18 2016-05-18 华南师范大学 Magnetic polyaniline/graphene composite material and preparation method and application thereof
CN106633070A (en) * 2016-12-30 2017-05-10 中国农业科学院农业质量标准与检测技术研究所 Metal-organic framework imprinted material and preparation method thereof
CN107513164A (en) * 2016-06-16 2017-12-26 中国科学院福建物质结构研究所 For Cr VI Anionic recognition and the backbone chain type imidazolium ion polymer of separation
CN108355613A (en) * 2018-03-02 2018-08-03 南京师范大学常州创新发展研究院 Magnetic covalent organic framework material and its preparation method and application
CN109342613A (en) * 2018-09-18 2019-02-15 山东省分析测试中心 A method of for analyzing phenols endocrine disruptors in beverage

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4439059A (en) * 1980-07-08 1984-03-27 Asahi Kasei Kogyo Kabushiki Kaisha Artificial reef unit
CN103724234A (en) * 2014-01-03 2014-04-16 万华化学集团股份有限公司 Method for preparing polyisocyanate containing biuret
CN105585711A (en) * 2015-12-18 2016-05-18 华南师范大学 Magnetic polyaniline/graphene composite material and preparation method and application thereof
CN107513164A (en) * 2016-06-16 2017-12-26 中国科学院福建物质结构研究所 For Cr VI Anionic recognition and the backbone chain type imidazolium ion polymer of separation
CN106633070A (en) * 2016-12-30 2017-05-10 中国农业科学院农业质量标准与检测技术研究所 Metal-organic framework imprinted material and preparation method thereof
CN108355613A (en) * 2018-03-02 2018-08-03 南京师范大学常州创新发展研究院 Magnetic covalent organic framework material and its preparation method and application
CN109342613A (en) * 2018-09-18 2019-02-15 山东省分析测试中心 A method of for analyzing phenols endocrine disruptors in beverage

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
《Covalent triazine-based frameworks/iron oxide for highly sensitive magnetic solid-phase extraction of phenolic pollutants in water samples》;Jin-Qing Ma等;《Journal of separation science》;20181231;第41卷;第1-2节 *
《Magnetic covalent triazine-based frameworks as magnetic solid-phase extraction adsorbents for sensitive determination of perfluorinated compounds in environmental water samples》;Ji-Yun Ren等;《Analytical and Bioanalytical Chemistry》;20181231;第410卷;实验部分 *
《Microwave-enhanced synthesis of magnetic porous covalent triazine-based framework composites for fast separation of organic dye from aqueous solution》;Wang Zhang等;《Journal of Hazardous Materials》;20111231;第186卷;实验部分 *
《过一硫酸盐的活化及其降解水中有机污染物机理的研究进展》;吴光锐等;《化工环保》;20181231;第38卷(第5期);第505-513页 *

Also Published As

Publication number Publication date
CN110204714A (en) 2019-09-06

Similar Documents

Publication Publication Date Title
CN110204714B (en) Magnetic covalent triazine framework material and preparation method and application thereof
Yang et al. Yolk-shell Fe3O4@ MOF-5 nanocomposites as a heterogeneous Fenton-like catalyst for organic dye removal
Rajabzadeh et al. Generation of Cu nanoparticles on novel designed Fe 3 O 4@ SiO 2/EP. EN. EG as reusable nanocatalyst for the reduction of nitro compounds
Sadeghzadeh et al. The reduction of 4-nitrophenol and 2-nitroaniline by the incorporation of Ni@ Pd MNPs into modified UiO-66-NH 2 metal–organic frameworks (MOFs) with tetrathia-azacyclopentadecane
CN104014316B (en) The method of tannic acid in the preparation of chitosan magnetic and adsorbed water
CN104525266B (en) Preparation method of metal-organic framework material photocatalyst and application
CN108579664A (en) Magnetic nanometer composite material and its preparation method and application based on two-dimensional layer material magadiite
CN106693935A (en) Method for preparing magnetic carbon material from core-shell metal organic framework
CN104248987A (en) Spherical montmorillonite mesoporous composite material, supported catalyst and preparation method and application thereof and preparation method of ethyl acetate
CN104248980A (en) Spherical diatomite mesoporous composite and supported catalyst, preparation method thereof and application thereof, and ethyl acetate preparation method
Nikoorazm et al. Synthesis and characterization of a Pd (0) Schiff base complex anchored on magnetic nanoporous MCM-41 as a novel and recyclable catalyst for the Suzuki and Heck reactions under green conditions
CN109317162B (en) High-efficiency heterogeneous Fenton-like catalyst MnFe2O4/SiO2Preparation method of (1)
CN111346609A (en) Adsorbing material for heavy metal dye-containing wastewater and preparation method thereof
CN112280052A (en) Hierarchical pore ZIF-8 material and preparation method and application thereof
Adam et al. Nanocomposite‐based inorganic‐organocatalyst Cu (II) complex and SiO2‐and Fe3O4 nanoparticles as low‐cost and efficient catalysts for aniline and 2‐aminopyridine oxidation
Gong et al. Manganese-phosphomolybdate molecular catalysts for the electron transfer reaction of ferricyanide to ferrocyanide
CN104248984B (en) The preparation method of spherical diatomite mesoporous composite material and loaded catalyst and its preparation method and application and ethyl acetate
CN102531994B (en) Method for synthesizing bismaleimide
CN109012629B (en) Method for preparing magnetic carboxymethyl beta-cyclodextrin polymer and application thereof
CN113578275A (en) For NOxManganese-cobalt binary metal-based MOF adsorbent for gas removal and preparation method thereof
Laayati et al. M-type SrFe12O19 ferrite: an efficient catalyst for the synthesis of amino alcohols under solvent-free conditions
CN113318768A (en) Composite photocatalyst and preparation method thereof
CN107245136B (en) A kind of ordered mesoporous polymer material and its preparation method and application
Tao et al. Preparing a highly dispersed catalyst supported on mesoporous microspheres via the self-assembly of amphiphilic ligands for the recovery of ultrahigh concentration wastewater
CN111995762A (en) Preparation method and application of dicarboxylic acid ligand Zn metal organic framework material

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant